Syzygium grande (sea apple)
Index
- Pictures
- Identity
- Summary of Invasiveness
- Taxonomic Tree
- Notes on Taxonomy and Nomenclature
- Description
- Plant Type
- Distribution
- Distribution Table
- History of Introduction and Spread
- Risk of Introduction
- Habitat
- Habitat List
- Biology and Ecology
- Climate
- Latitude/Altitude Ranges
- Air Temperature
- Rainfall
- Rainfall Regime
- Soil Tolerances
- Means of Movement and Dispersal
- Pathway Causes
- Pathway Vectors
- Impact Summary
- Impact: Economic
- Impact: Environmental
- Risk and Impact Factors
- Uses
- Uses List
- Wood Products
- Prevention and Control
- Gaps in Knowledge/Research Needs
- References
- Contributors
- Distribution Maps
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Top of pageIdentity
Top of pagePreferred Scientific Name
- Syzygium grande (Wight) Walp.
Preferred Common Name
- sea apple
Other Scientific Names
- Eugenia grandis Wight
- Eugenia laosensis Gagnep.
- Eugenia montana Wight
- Jambosa firma Blume
- Jambosa grandis (Wight) Blume
- Syzygium firmum (Blume) Thwaites
- Syzygium laosense (Gagnep.) Merr. & L.M.Perry
- Syzygium megalophyllum Merr. & L.M.Perry
- Syzygium montanum Thwaites & Hook.f.
Local Common Names
- Bangladesh: bhattijam; dhakijam
- India: jam; jamuk
- Indonesia: klokos
- Malaysia: jambu ayer laut; jambu laut; jemba; kerian acheh; kerian ayer; ubah
- Malaysia/Peninsular Malaysia: jambu air laut; jambu jembah; kelat jambu
- Myanmar: thabyay-kyee; thabyegyi; thabye-pinbwa; thabye-ywet-gyi; toungthabyay
- Thailand: mao; wa-dong; yamu-yimma
Trade name
- jam
- jaman
Summary of Invasiveness
Top of pageS. grande is listed in the Global Compendium of Weeds as a cultivated and naturalized species (Randall, 2012). While not currently known to be invasive, it continues to be actively cultivated for use as a firebreak and regeneration species in Singapore and Bangladesh, is spread by biotic and abiotic agents, and is known to be naturalized in places beyond its native range, demonstrating its potential for invasiveness (Hossein, 2003; Islam, 2003; Daehler and Baker, 2006; Shono et al., 2007; Randall, 2012). Based on current literature S. grande is not a high-risk species, but considering that several other Syzygium species are known to be weedy or invasive and even threats to native biodiversity, monitoring of this species may be required in the future.
Taxonomic Tree
Top of page- Domain: Eukaryota
- Kingdom: Plantae
- Phylum: Spermatophyta
- Subphylum: Angiospermae
- Class: Dicotyledonae
- Order: Myrtales
- Family: Myrtaceae
- Genus: Syzygium
- Species: Syzygium grande
Notes on Taxonomy and Nomenclature
Top of pageSyzygium is a tropical genus of the Myrtle family Myrtaceae consisting of over 1000 species with greatest diversity in Malesia and the Old World tropics. Some economically significant members of this genus include the clove tree, S. aromaticum, the rose-apple, S. jambos, and the Malay-apple, S. malaccense.
There has been past taxonomic confusion between the genera Syzygium and Eugenia, but the center of diversity for Eugenia is in the Neotropics. Linnaeus originally described several species under the name Eugenia, named in honour of Prince Eugene of Savoy (1663-1736), a patron of botany and horticulture (Britton, 1918). The species Syzygium grande was first described by Wight under two separate names, Eugenia grandis and E. montana, in 1841; the names S. grande and E. grandis had previously been listed in an 1831 publication by Wallich, but had not been described. Two years later, in 1843, Eugenia grandis was moved to the Syzygium genus by Walpers, resulting in the currently accepted taxonomic name Syzygium grande (Wight) Welp. (IPNI, 2015).
Description
Top of pageLarge tree, up to 30 m tall. Bark is rough with shallow fissures, grayish buff or pinkish in colour with inner bark pale pink to dark reddish and pale yellow near the surface. Leaves are broadly elliptical (10-25 cm x 6-12 cm) with up to 20 well-spaced secondary veins in a pinnate arrangement, its veins appearing invisible near the leaf margin. Flowers are 2.5-3 cm when expanded, very fragrant, petals and stamens white. Fruits are somewhat globular, urn-shaped to ellipsoid berries, apparently green when ripe, 1-2 cm in length, containing a single seed 5-7 mm in size (Henderson, 1949; Daehler and Baker, 2006; PIER, 2015).
Distribution
Top of pageS. grande is considered native to the Old World tropics, probably the Malay Peninsula, and it is widespread and “relatively common throughout much of mainland Southeast Asia” (Parnell et al., 2007). It was listed in the Western Australian Herbarium’s Florabase (2015) (as syn. E. grandis) as native to Western Australia, but has also been reported as a useful but not endemic species (Maiden, 1899). In the Neotropics, the species is known to occur in parts of Hawaii (Daehler and Baker, 2006). It is also present in parts of the West Indies with specimens having been collected in Cuba, Costa Rica, Panama, and Puerto Rico beginning in the 1930s (US National Herbarium; New York Botancial Garden, 2015), but as of 2000 it was yet ‘scarcely cultivated’ in Puerto Rico (Liogier and Martorell, 2000). The species was not listed in Broome et al.’s (2007) work on the Eastern Caribbean, or in species lists from the Guinea Shield (Funk et al., 2007), Micronesia (Wagner et al., 2015) or the Marquesas (Wagner and Lorence, 2015), suggesting the species is, if present, not common in these places.
Distribution Table
Top of pageThe distribution in this summary table is based on all the information available. When several references are cited, they may give conflicting information on the status. Further details may be available for individual references in the Distribution Table Details section which can be selected by going to Generate Report.
Last updated: 10 Jan 2020Continent/Country/Region | Distribution | Last Reported | Origin | First Reported | Invasive | Planted | Reference | Notes |
---|---|---|---|---|---|---|---|---|
Africa |
||||||||
Seychelles | Present | Introduced | Naturalized | Naturalised | ||||
Asia |
||||||||
Bangladesh | Present | Native | ||||||
Brunei | Present | Native | ||||||
Cambodia | Present | Native | ||||||
China | Present | Native | South-central China | |||||
India | Present | Native | ||||||
-Andaman and Nicobar Islands | Present | Native | ||||||
-Assam | Present | Native | ||||||
-Meghalaya | Present | |||||||
Indonesia | Present | Present based on regional distribution. | ||||||
-Sumatra | Present | Native | ||||||
Japan | Present | Planted | ||||||
Malaysia | Present | Planted | ||||||
-Peninsular Malaysia | Present | Native | Common along coastal edges of Jarak Island, Malacca Strait | |||||
Myanmar | Present | Native | ||||||
Singapore | Present | Native | Common | |||||
Sri Lanka | Present | Native | ||||||
Thailand | Present | |||||||
Vietnam | Present | Native | ||||||
North America |
||||||||
Costa Rica | Present | Specimen collected in 1993 | ||||||
Cuba | Present | Specimens collected in 1930 and 1932 | ||||||
Panama | Present | Specimen collected in 1986 | ||||||
Puerto Rico | Present | Introduced | ||||||
United States | Present | Present based on regional distribution. | ||||||
-Hawaii | Present | Introduced | Naturalized | Naturalised around Lyon Arboretum, Aihualama Island as of 2006 | ||||
Oceania |
||||||||
Australia | Present | Present based on regional distribution. | ||||||
-Western Australia | Present | Native |
History of Introduction and Spread
Top of pageS. grande is considered native to the Old World tropics with natural populations in Bangladesh, India, Indonesia, Malaysia, Myanmar and Thailand, often being grown on plantations in these places for timber production. It has also been actively cultivated in Bangladesh and Singapore to aid in repopulating deforested areas as its mature wood is fire-resistant (Hossein, 2003; Islam, 2003; Shono et al., 2007; Rahman et al., 2011; Govaerts, 2015). It was listed in the Western Australian Herbarium’s FloraBase (2015) (as syn. E. grandis) as native to Western Australia and was listed as being cultivated in the Melbourne Botanic Gardens in 1883 (Guilfoyle, 1883), but Maiden (1899) reported it as a timber species not native to Australia.
In Hawaii, where the species can be found growing on coastal edge forests, it was apparently first grown in the Lyon Arboretum in 1932, with a report of its naturalized state around the Arboretum first reported in 2006 (Daehler and Baker, 2006); there were observed “hundreds of seedlings and saplings... mostly within 100 m of the original plantings in both Haukulu and ‘Aihualama” and “thickets of saplings in unmanaged forests”.
Date of introduction to the West Indies is uncertain but, similarly to the case of Hawaii, it may have occurred within the last century. The species was not listed in floras from the late nineteenth and early twentieth centuries, but specimens were collected in Cuba in 1930 and 1932 (Smithsonian Museum of Natural History, 2015). Liogier and Martorell (2000) described it as “scarcely cultivated” in Puerto Rico.
Risk of Introduction
Top of pageRisk of introduction for this species is currently low, as it is not yet considered weedy or invasive (Randall, 2012; PIER, 2015). It is known to naturalize in non-native habitats, but this has so far only been observed to occur in areas immediately surrounding plantations or forested places where it had intentionally been planted for forest regeneration or as a timber source (Hossein, 2003; Islam, 2003; Daehler and Baker, 2006). Its seeds are viable and are dispersed by biotic and abiotic vectors, and the species is capable of reproducing vegetatively. Considering the invasiveness of other Sygyzium species and serious threat they have reportedly posed to native biodiversity, S. grande may require monitoring and re-evaluation in the later future.
Habitat
Top of pageOn the Malay Peninsula, where it is native, S. grande has been reported to occur wild on sandy and rocky sea coasts, and is widely planted inland as a roadside tree (Henderson, 1949; PIER, 2015). In Bangladesh, the species has been actively planted to repopulate deforested areas, for use as timber, and to act as firebreak trees; it has been planted in managed forests, marginal land areas such as roadsides, and plantations (Hossein, 2003; Islam, 2003). In Singapore, S. grande occurs as a coastal tree and can be commonly found on sandy and rocky shores, and is also widely planted as a wayside tree (National University of Singapore, 2015). The species also occurs in the forests of Yauco, Puerto Rico (Liogier and Martorell, 2000).
Habitat List
Top of pageCategory | Sub-Category | Habitat | Presence | Status |
---|---|---|---|---|
Terrestrial | Managed | Cultivated / agricultural land | Present, no further details | Productive/non-natural |
Terrestrial | Managed | Managed forests, plantations and orchards | Present, no further details | Natural |
Terrestrial | Managed | Managed forests, plantations and orchards | Present, no further details | Productive/non-natural |
Terrestrial | Managed | Disturbed areas | Present, no further details | Productive/non-natural |
Terrestrial | Managed | Rail / roadsides | Present, no further details | Natural |
Terrestrial | Managed | Rail / roadsides | Present, no further details | Productive/non-natural |
Terrestrial | Natural / Semi-natural | Natural forests | Present, no further details | Productive/non-natural |
Littoral | Coastal areas | Present, no further details | Natural | |
Littoral | Coastal areas | Present, no further details | Productive/non-natural |
Biology and Ecology
Top of pageS. grande has a good regeneration capacity. Synchronous flowering can be observed at the onset of wet spells, with greater intensity of flowering if this follows a long dry period. The flowers attract birds, bees and butterflies, but are probably pollinated by bats (Singapore National Parks Board, 2013). There are about 70 fruits per kilogram, each containing a single seed. Seed viability is short (15-25 days). About 60-70% of seeds germinate after direct sowing. In nurseries, seed germination can increase to 75-80% when raised in polybags. It coppices well when young, but coppicing ability declines with age. It can also be propagated vegetatively through grafting and air-layering.
Environmental Requirements
The species commonly occurs along coastal areas and withstand soils ranging from rocky, sandy, and unfertile to fertile (Henderson, 1949; National University of Singapore, 2015; PIER, 2015).
Climate
Top of pageClimate | Status | Description | Remark |
---|---|---|---|
Af - Tropical rainforest climate | Preferred | > 60mm precipitation per month | |
Am - Tropical monsoon climate | Preferred | Tropical monsoon climate ( < 60mm precipitation driest month but > (100 - [total annual precipitation(mm}/25])) | |
Aw - Tropical wet and dry savanna climate | Preferred | < 60mm precipitation driest month (in winter) and < (100 - [total annual precipitation{mm}/25]) |
Latitude/Altitude Ranges
Top of pageLatitude North (°N) | Latitude South (°S) | Altitude Lower (m) | Altitude Upper (m) |
---|---|---|---|
25 | -10 | 3 | 300 |
Air Temperature
Top of pageParameter | Lower limit | Upper limit |
---|---|---|
Absolute minimum temperature (ºC) | 6 | |
Mean annual temperature (ºC) | 23 | 28 |
Mean maximum temperature of hottest month (ºC) | 22 | 40 |
Mean minimum temperature of coldest month (ºC) | 6 | 18 |
Rainfall
Top of pageParameter | Lower limit | Upper limit | Description |
---|---|---|---|
Dry season duration | 0 | 4 | number of consecutive months with <40 mm rainfall |
Mean annual rainfall | 2000 | 5000 | mm; lower/upper limits |
Soil Tolerances
Top of pageSoil drainage
- free
- impeded
Soil reaction
- acid
- neutral
Soil texture
- heavy
- light
- medium
Special soil tolerances
- infertile
- shallow
Means of Movement and Dispersal
Top of pageNatural Dispersal (Non-Biotic)
Seed dispersal by water is possible: the species thrives in coastal edge forests of its native Malay range as well as in Hawaii and Singapore.
Vector Transmission (Biotic)
Seed can be dispersed by animals; the species’ fruits are eaten by bats (Wyatt-Smith, 1953; National University of Singapore, 2015), as well as monkeys and squirrels (Ridley, 1894).
Accidental Introduction
The species is known to have naturalized beyond its native range in places where it had been cultivated for use in agroforestry and revegetation (Randall, 2012).
Intentional Introduction
S. grande has been cultivated for use in agroforestry and revegetation, most notably in Bangladesh and Singapore (Hossein, 2003; Islam, 2003; Shono et al., 2007; Randall, 2012).
Pathway Causes
Top of pageCause | Notes | Long Distance | Local | References |
---|---|---|---|---|
Breeding and propagation | Species has been actively utilized in plantation and reforestation programmes | Yes | Yes | Islam, 2003; Shono et al., 2007 |
Digestion and excretion | Fruits are eaten by bats, monkeys, and squirrels | Yes | Ridley, 1894; Wyatt Smith, 1953 | |
Forestry | Species is cultivated as part of teak and timber programme in Bangladesh | Yes | Yes | Hossain, 2003 |
Habitat restoration and improvement | Species has been actively utilized in plantation and reforestation programmes | Yes | Yes | Islam, 1984; Rahman et al., 2011 |
Medicinal use | Seeds, fruit, and bark are used in local traditional medicine | Yes | National University of Singapore, 2015; Rahman, 1977 | |
Timber trade | Yes | Yes | Hossain, 2003; Islam, 2003; Shono et al., 2007 |
Pathway Vectors
Top of pageVector | Notes | Long Distance | Local | References |
---|---|---|---|---|
Debris and waste associated with human activities | Seeds, fruit, and bark are used locally in traditional medicine | Yes | Rahman et al., 2011 | |
Floating vegetation and debris | Water dispersal is possible as species grows along coastal edge forests | Yes | Henderson, 1949; National University of Singapore, 2015; PIER, 2015; Wyatt Smith, 1953 | |
Water | Water dispersal is possible as species grows along coastal edge forests | Yes | Henderson, 1949; National University of Singapore, 2015; PIER, 2015; Wyatt Smith, 1953 |
Impact Summary
Top of pageCategory | Impact |
---|---|
Economic/livelihood | Positive |
Environment (generally) | Positive |
Human health | Positive |
Impact: Economic
Top of pageS. grande has been cultivated in tropical Asia for the commercial production of timber and for use as a firebreak tree, especially in areas that had been severely deforested and are susceptible to brush fires. As the species appears to naturalize in the areas immediately surrounding where it was originally planted (Daehler and Baker, 2006; PIER, 2015), its introduction and presumably limited spread to non-native areas would not be expected to have a negative economic impact.
Impact: Environmental
Top of pageNaturalization of the species appears to be limited to areas surrounding plantations and places where it had been originally intentionally planted (Daehler and Baker, 2006; PIER, 2015); currently, there has been no report of its invasion or negative economic or environmental impact, but this is an area for future research.
Risk and Impact Factors
Top of page- Abundant in its native range
- Tolerates, or benefits from, cultivation, browsing pressure, mutilation, fire etc
- Pioneering in disturbed areas
- Long lived
- Has propagules that can remain viable for more than one year
- Modification of fire regime
- Highly likely to be transported internationally deliberately
Uses
Top of pageEconomic Value
The species has been cultivated in plantations for timber production, by itself or mixed in with teak or other tree species. Its wood is used for a number of products including posts, poles, roundwood, and other construction materials (Islam, 2003).
Social Benefit
Various members of the Syzygium genus are used in local medical traditions, and some, such as the Malay apple and the date plum, are cultivated for their edible fruits. S. grande is known to be used medicinally in Bangladesh; its mature fruit, seeds, and bark are harvested and used locally to treat cases of coughs, piles, tooth diseases, dysentery, bronchitis, and diabetes (Rahman et al., 2011).
The fruits of S. grande, while not known to be grown for food, are often eaten by animals such as monkeys, bats, and squirrels which aid in the dispersal of the seeds (Ridley, 1894; Wyatt-Smith, 1953; National University of Singapore, 2015).
Environmental Services
In Singapore and Bangladesh, S. grande has been cultivated in areas that have suffered major deforestation and are susceptible to brush fires, as S. grande is a good firebreak tree (Islam, 2003; Shono et al., 2007).
Uses List
Top of pageEnvironmental
- Agroforestry
- Firebreak
- Revegetation
Materials
- Wood/timber
Medicinal, pharmaceutical
- Traditional/folklore
Wood Products
Top of pageBoats
Charcoal
Containers
- Boxes
- Tanks
- Vats
Furniture
Pulp
- Short-fibre pulp
Railway sleepers
Roundwood
- Building poles
- Posts
- Stakes
- Transmission poles
Sawn or hewn building timbers
- Beams
- Bridges
- Carpentry/joinery (exterior/interior)
- Engineering structures
- Exterior fittings
- Fences
- Flooring
- For heavy construction
- For light construction
- Gates
- Wall panelling
Vehicle bodies
Veneers
Wood-based materials
- Fibreboard
- Hardboard
- Particleboard
- Plywood
Woodware
- Industrial and domestic woodware
- Tool handles
Prevention and Control
Top of pageDue to the variable regulations around (de)registration of pesticides, your national list of registered pesticides or relevant authority should be consulted to determine which products are legally allowed for use in your country when considering chemical control. Pesticides should always be used in a lawful manner, consistent with the product's label.
Physical/Mechanical Control
Physical control methods such as cutting down or frilling (removal of bark completely around the base of the tree trunk) have been used in combination with herbicide applications in vigorous efforts to control some Syzygium species that have proved invasive threats to native flora of places such as Hawaii, the Galapagos Islands, and Pitcairn Islands (ISSG, 2015). Physical removal of trees and replacing them with native species has also been a reported method for an invasive Syzygium species (S. jambos) in Costa Rica (Avalos et al., 2006).
Chemical Control
Syzygium species can be controlled by herbicides, and in places where species have become serious threats to native flora, a combination of physical and chemical control methods have been reported. Syzygium cumini, for example, forms a dense cover and because of its extensive cultivation as a fruit tree, has become very invasive in Hawaii, the Cook Islands, and French Polynesia; vigorous efforts are being undertaken in Hawaii to remove the species through chemical control (ISSG, 2015). Syzygium jambos is likewise an invasive species on several Pacific islands, and has been reportedly controlled by applying herbicides (picloram and metsulfuron-methyl at 5-10%) (ISSG, 2015).
Gaps in Knowledge/Research Needs
Top of pageS. grande is currently a low risk species. There is as yet no evidence that it has become invasive in non-native places where it has been introduced, cultivated, and naturalized, but this may change considering its role as a firebreak tree in tropical forest recovery programmes such as those in Singapore and Bangladesh. Although based on current literature it is a species of low concern, an assessment of its impact on local biodiversity is recommended, considering several related species are known to be weedy and invasive.
References
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Anwar MS, 1989. Silviculture of Dhakijam (Syzygium grande). Review paper No. 217. Chittagong, Bangladesh: Institute of Forestry and Environment Sciences, Chittagong University. (unpublished).
Avalos G; Hoell K; Gardner J; Anderson S; Lee C, 2006. Impact of the invasive plant Syzygium jambos (Myrtaceae) on patterns of understory seedling abundance in a Tropical Premontane Forest, Costa Rica. Rev. Biol. Trop (International Journal of Tropical Biology), 54(2):415-421.
Bangladesh Standard and Testing Institution, 1983. Bangladesh Standard Specification for General Purposes. Dhaka, Bangladesh: Bangladesh Standard and Testing Institution.
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Britton NL, 1918. Flora of Bermuda. New York, USA: Charles Scribner's Sons. 585 pp.
Broome R; Sabir K; Carrington S, 2007. Plants of the Eastern Caribbean. Online database. Barbados: University of the West Indies. http://ecflora.cavehill.uwi.edu/index.html
Chong KY; Tan HTW; Corlett RT, 2009. A checklist of the total vascular plant flora of Singapore: native, naturalised and cultivated species. Singapore: Raffles Museum of Biodiversity Research, National University of Singapore, 273 pp. http://lkcnhm.nus.edu.sg/nus/pdf/PUBLICATION/LKCNH%20Museum%20Books/LKCNHM%20Books/flora_of_singapore_tc.pdf
Daehler CC; Baker RF, 2006. New records of naturalized and naturalizing plants around Lyon Arboretum, Manoa Valley, O'ahu. Part 1: Articles. Records of the Hawaii Biological Survey for 2004-2005, Bishop Museum Occasional Papers, 87:3-18.
Das D, 1970. An Anatomical Study of Jam (Syzygium spp.). Timbers of East Pakistan. Bull. 1., Wood Anatomy Series. Chittagong, Bangladesh: Bangladesh Forest Research Institute.
Dochnal EF, 1987. Review of Provisional Yield Tables Set-up. Assistance to the Forestry Sector of Bangladesh - Phase II. FAO Project BGD/85/085. Rome, Italy: Food and Agriculture Organizations of United Nations.
Flora Mesoamericana, 2015. Flora Mesoamericana. St. Louis, Missouri, USA: Missouri Botanical Garden. http://www.tropicos.org/Project/fm
Ginoga B, 1996. Machining properties of nine wood species originated from West Nusa Tenggara. Buletin Penelitian Hasil Hutan, 14(2):47-51; 7 ref.
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Guilfoyle WR, 1883. Catalogue of Plants Under Cultivation in the Melbourne Botanic Gardens. Melbourne, Australia: Ferres, Government Printer, 200 pp.
Henderson MR, 1949. The genus Eugenia (Myrtaceae) in Malaya. Gardens' Bulletin, 12(1):1-293.
Hossain MK, 2003. Growth performance and critics of exotics in the plantation forestry of Bangladesh. In: FAO XII World Forestry Congress, 2003, Quebec City, Canada. Chittagong, Bangladesh: Institute of Forestry and Environmental Sciences, Chittagong University. http://www.fao.org/docrep/ARTICLE/WFC/XII/0113-B1.HTM
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Islam SS, 2003. State of forest genetic resources, conservation and management in Bangladesh, Working Paper FGR/68E. Rome, Italy: Forest Resources Development Service, Forest Resources Division, FAO. [Forest Genetic Resources Working Papers.] http://www.fao.org/forestry/6646-04322ad252f01b26949a2f126cec49057.pdf
ISSG, 2015. Global Invasive Species Database (GISD). Invasive Species Specialist Group of the IUCN Species Survival Commission. http://www.issg.org/database/welcome/
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PIER, 2015. Pacific Islands Ecosystems at Risk. Honolulu, USA: HEAR, University of Hawaii. http://www.hear.org/pier/index.html
Rahman MA, 1977. Forest Pathology in Bangladesh: an introduction. Paper presented in the Second Bangladesh Annual Science Conference, held at Bangladesh Agricultural University, Mymensingh, Bangladesh, 8-12 January 1977. Mymensingh, Bangladesh: Bangladesh Agricultural University.
Randall RP, 2012. A Global Compendium of Weeds. Perth, Australia: Department of Agriculture and Food Western Australia, 1124 pp. http://www.cabi.org/isc/FullTextPDF/2013/20133109119.pdf
Ridley HN, 1894. On the dispersal of seeds by mammals. Journal of the Straits Branch of the Royal Asiatic Society, 25(Jan 1894):11-32.
Sattar MA; Akhtaruzzaman AFM; Siddiqi AB; Alam MK; Ali M; Khaleque MA, 1992. End-use classification of lesser used or unused wood species. Chittagong, Bangladesh: Forest Products Branch, Bangladesh Forest Research Institute.
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USDA-NRCS, 2015. The PLANTS Database. Baton Rouge, USA: National Plant Data Center. http://plants.usda.gov/
Wagner WL; Herbst DR; Tornabene MW; Weitzman A; Lorence DH, 2015. Flora of Micronesia website. Washington DC, USA: Smithsonian Institution. http://botany.si.edu/pacificislandbiodiversity/micronesia/index.htm
Wagner WL; Lorence DH, 2015. Flora of the Marquesas Islands website. Washington DC, USA: Smithsonian Institution. http://botany.si.edu/pacificislandbiodiversity/marquesasflora/index.htm
Western Australian Herbarium, 2015. FloraBase. Australia: Western Australian Herbarium. http://florabase.dec.wa.gov.au/
Yakub M; Bhattacharjee DK; Ali MO, 1972. Strength Properties of some Bangladesh Timber Species. Bulletin 2. Chittagong, Bangladesh: Bangladesh Forest Research Institute.
Distribution References
CABI, Undated. Compendium record. Wallingford, UK: CABI
CABI, Undated a. CABI Compendium: Status inferred from regional distribution. Wallingford, UK: CABI
CABI, Undated b. CABI Compendium: Status as determined by CABI editor. Wallingford, UK: CABI
Chong KY, Tan HTW, Corlett RT, 2009. A checklist of the total vascular plant flora of Singapore: native, naturalised and cultivated species., Singapore, Raffles Museum of Biodiversity Research, National University of Singapore. 273 pp. http://lkcnhm.nus.edu.sg/nus/pdf/PUBLICATION/LKCNH%20Museum%20Books/LKCNHM%20Books/flora_of_singapore_tc.pdf
Daehler CC, Baker RF, 2006. New records of naturalized and naturalizing plants around Lyon Arboretum, Manoa Valley, O'ahu. Part 1: Articles. Records of the Hawaii Biological Survey for 2004-2005. In: Bishop Museum Occasional Papers, 87 3-18.
Flora Mesoamericana, 2015. Flora Mesoamericana., St. Louis, Missouri, USA: Missouri Botanical Garden. http://www.tropicos.org/Project/fm
Govaerts R, 2015. World Checklist of Myrtaceae., Richmond, UK: Royal Botanic Gardens. http://apps.kew.org/wcsp/
Kress WJ, Defilipps RA, Farr E, Kyi DYY, 2003. A checklist of the trees, shrubs, herbs, and climbers of Myanmar. In: Contributions from the United States National Herbarium, 45 1-590.
Liogier HA, Martorell LF, 2000. Flora of Puerto Rico and adjacent islands: a systematic synopsis, 2nd edition revised., San Juan, Puerto Rico: La Editorial, University of Puerto Rico. 382 pp.
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Singapore National Parks Board, 2013. Flora and Fauna Web., Singapore National Parks, Singapore: National Parks Board. https://florafaunaweb.nparks.gov.sg/Home.aspx
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Contributors
Top of page08/10/2015 Original text by:
Marianne Jennifer Datiles, Department of Botany-Smithsonian NMNH, Washington DC, USA
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